首页> 外文会议>2008 American Water Works Association annual conference amp; exposition (ACE08) >The Formation of Halonitromethanes in Wastewater Treatment Plant Effluents
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The Formation of Halonitromethanes in Wastewater Treatment Plant Effluents

机译:污水处理厂废水中卤代硝基甲烷的形成

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The objectives of this work were to investigate the formation of Halonitromethanes (HNMs) atrnwastewater treatment plant effluents under different disinfection conditions, to study the effect ofrnultraviolet light (UV) disinfection in wastewater treatment facilities on HNM formation potentials, and tornquantify the actual occurrence of HNMs at the effluents of selected wastewater treatment plants. Thernresults showed that among the five disinfection scenarios tested, HNM yields per DOC were in the orderrnof ozonation-chlorination > ozonation-chloramination > chlorination > chloramination > ozonation.rnPre-ozonation prior to chlorination and chloramination significantly increased HNM formation, whilernozonation alone did not produce any HNMs. Therefore, HNM formation is expected to be problematicrnmainly in treatment plants using ozonation followed by chlorination. The use of chloramines afterrnozonation significantly decreased HNM formation compared to using chlorine after ozonation.rnChloramination produced the least amount of HNMs of all the disinfection scenarios tested. Despite somernof its disadvantages (e.g. weak disinfectant, nitrification problems in distribution systems), it appears thatrnchloramination produces significantly lower amounts of HNMs as well as regulated trihalomethanes andrnhaloacetic acids than chlorination. The typical UV disinfection conditions in full-scale municipalrnwastewater treatment plants (WWTPs) using low pressure lamps did not change the HNM formationrnpotential (compared to the same water prior to UV disinfection) in wastewater effluents. Also, actualrnHNM concentrations at the effluents of full-scale WWTPs using chlorine disinfection were below 2 μg/L,rnwhile no HNM formation was observed at the effluents of WWTPs using UV disinfection. It appears thatrnat the typical disinfectant doses and detention times of wastewater disinfection processes, trace amountsrnof HNMs will form. However, WWTPs still release HNMs (and other DBP) precursors, as observed withrnthe formation potential tests, to downstream users.
机译:这项工作的目的是调查不同消毒条件下废水处理厂卤代硝基甲烷(HNMs)的形成,研究废水处理设施中紫外线(UV)消毒对HNM形成潜能的影响,并量化HNMs的实际发生选定的废水处理厂的废水。结果表明,在所测试的五个消毒方案中,每个DOC的HNM产量按以下顺序进行:臭氧氧化-氯化>>>臭氧氧化-氯化>氯化>氯化>臭氧化。不产生任何HNM。因此,预期在使用臭氧化然后氯化的处理厂中,HNM的形成将是主要问题。与臭氧化后的氯相比,在氮磺酰化后使用氯胺可显着减少HNM的形成。在所有测试的消毒方案中,氯胺化产生的HNM数量最少。尽管存在某些缺点(例如,消毒剂弱,分配系统中存在硝化问题),但与氯化相比,氯胺化产生的HNM以及受调节的三卤代甲烷和卤代卤代乙酸的含量要低得多。在使用低压灯的大型市政污水处理厂(WWTP)中,典型的紫外线消毒条件不会改变废水中的HNM形成潜能(与紫外线消毒之前的相同水相比)。此外,使用氯消毒的全尺寸污水处理厂废水中的实际rnm浓度低于2μg/ L,而使用紫外线消毒的污水处理厂废水中未观察到HNM的形成。看来,在废水消毒过程的典型消毒剂量和滞留时间下,会形成微量的HNM。但是,正如形成潜力测试所观察到的那样,污水处理厂仍然向下游用户释放HNM(和其他DBP)前体。

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